CARRIER FOR NOx REDUCTION CATALYST

ABSTRACT

A NOx reduction catalyst carrier yields a NOx reduction catalyst with an improved permissible dose of poisoning substances such as arsenic. More specifically, the present invention relates to a NOx reduction catalyst carrier comprising TiO 2 , having a honeycomb structure and having a specific surface area greater than 100 m 2 /g.

TECHNICAL FIELD

The present invention relates to a carrier for a NOx reduction catalyst used in various types of NOx reduction apparatuses. More specifically, the present invention relates to a carrier for a NOx reduction catalyst suitable for use in a NOx reduction apparatus for flue gases from coal-fired boilers.

BACKGROUND ART

As a method for removing nitrogen oxides from flue gases emitted from stationary emission sources such as thermal power plants, an ammonia-added selective catalytic reduction method has been applied, which uses a catalyst carrying V₂O₅, WO₃, and MoO₃ as active ingredients on a TiO₂-based catalyst carrier. In this method, NH₃ is added as a reductant to cause a NOx reduction reaction (4NO+4NH₃+O₂→4N₂+6H₂O) and V, W, and Mo supported on solid acid sites of TiO₂ act as active sites.

When a V₂O₅/TiO₂-based catalyst is used in the reduction of NOx from flue gases containing nitrogen oxides emitted in a case in which a coal or a heavy oil is used as the fuel, the activity of such a catalyst degrades over time. The degradation of the activity of a catalyst is due to a very small quantity of poisoning components contained in flue gases, such as As and Ca, accumulating on the catalyst and covering the catalyst active sites. In particular, As contained in flue gases is As₂O₃ with a high vapor pressure and is oxidized on the catalyst to be converted into As₂O₅ with a low vapor pressure (As₂+O₃+O₂→As₂O₅). This As₂O₅ reacts at the solid acid sites, and thus the catalyst activity is lost. Accordingly, when a low-grade coal including a large quantity of arsenic (As), which is a poisoning substance that may considerably affect the catalyst, is used as the fuel, the deterioration of the catalyst occurring due to the rapid loss of solid acid sites caused by As becomes highly problematic.

Incidentally, it has been blown that when an oxide is composited, the solid acid content of the complex oxide usually becomes higher than that of a single-element oxide, although this depends on the type of the element included in the oxide. Focusing on this finding, the inventors have made an attempt to improve the resistance of a catalyst to As by increasing the permissible dose of As by increasing the content of solid acid in a two-component system based on TiO₂, such as a TiO₂/SiO₂ system (refer to Patent Literature 1, for example).

CITATION LIST Patent Literature

-   [Patent Literature 1] Japanese Patent Application Publication No.     11-42433

DISCLOSURE OF THE INVENTION Problems to be Solved by the Invention

The present invention has been made in consideration of the above-described circumstances, and an object of the present invention is therefore to provide a NOx reduction catalyst carrier capable of obtaining a NOx reduction catalyst with a further improved permissible dose of poisoning substances such as arsenic.

Means for Solving the Problems

In order to improve the resistance of a catalyst to poisoning by As in a system containing Ti, the inventors have focused attention on the above-described solid acid content, and also on a specific surface area, which is not correlated with the solid acid content.

More specifically, a NOx reduction catalyst carrier according to the present invention comprises TiO₂, has a honeycomb structure, and has a specific surface area greater than 100 m²/g.

Effects of the Invention

By using the NOx reduction catalyst carrier according to the present invention, a NOx reduction catalyst with a further improved permissible dose of a poisoning substance such as arsenic can be Obtained.

BRIEF DESCRIPTION OF DRAWINGS

FIG. 1 illustrates an example of NOx reduction catalyst carrier having a honeycomb structure.

FIG. 2 is a graph illustrating a correlation between degrees of deterioration of honeycomb catalysts for comparison and honeycomb catalysts according to Examples 1 to 9, which may occur due to poisoning by gases containing As, and specific surface areas of carriers used for the catalysts.

DESCRIPTION OF THE EMBODIMENTS

The present invention will be described in detail below. Note that the present invention is not limited to the embodiments described below.

A NOx reduction catalyst carrier according to the present invention comprises TiO₂ and has a honeycomb structure. Furthermore, the specific surface area thereof measured for a NOx reduction catalyst carrier molded so as to have a honeycomb structure is greater than 100 m²/g. With such a large specific surface area, the permissible quantity of adsorbable As is increased. Thus, the resistance to poisoning by As can be improved. Accordingly, an inflow of As into portions on a downstream side of a NOx reduction catalyst can be inhibited. It becomes more preferable if the specific surface area becomes greater. The specific surface area is particularly preferably 100 to 160 m²/g.

The specific surface area is a value measured by a nitrogen gas adsorption method.

The expression “comprise(s) TiO₂” herein refers to a concept including any of a case in which TiO₂ alone is comprised, a case in which Ti constitutes a complex oxide together with other elements, and a case in which TiO₂ is comprised as a mixture.

The NOx reduction catalyst carrier according to the present invention has a honeycomb structure. More specifically, the NOx reduction catalyst carrier according to the present invention preferably has a honeycomb structure having a plurality of through holes as reaction flow paths. Examples of such NOx reduction catalyst carriers include a carrier illustrated in FIG. 1, for example. However, the NOx reduction catalyst carrier is not limited to this. The honeycomb structure is not limited to a structure with a rectangular cross section. For example, the honeycomb structure may include a circular cross section, an elliptic cross section, a triangular cross section, a pentagonal cross section, a hexagonal cross section, or the like.

The carrier according to the present invention is preferably a complex oxide comprising one or two or more elements selected from the group consisting of Si, B. P. Zr, and W (hereinafter referred to as “element(s) M”), in addition to Ti. Because any of the above-described elements M to be composited with Ti is an element that is hardly poisoned by As included in flue gases, the element M is suitable for a NOx reduction catalyst.

If a complex oxide comprising two or more elements M in addition to Ti is to be prepared, it is preferable to add other elements to Ti and Si which are base materials. If a complex oxide comprises two or more elements M, a carrier with the resistance to poisoning by As as high as or higher than that achieved when one element is composited with Ti according to the specific surface area can be obtained.

In the case of a two-component system, the ratio by weight of TiO₂ and the oxide of the element M (hereinafter referred to as an “M oxide”) comprised in the carrier ranges preferably from 50:50 to 99:1. If the ratio of M oxide is below the above-described range, the effect of using the complex oxide may be lost. On the other hand, if the ratio of M oxide exceeds the above-described range, Ti and M may be bonded side by side via oxygen (—Ti—O-M-). As a result, the effect of forming acidic sites, which are sites having acidity imparted due to Charges biased on the surface of the solid body, may not be accelerated, and a catalyst with a satisfactory NOx reduction performance may not be obtained because of the low TiO₂ ratio. Preferable ranges for respective oxides are as follows: TiO₂:SiO₂=80:20 to 99:1, TiO₂:P₂O₅=50:50 to 99:1, TiO₂:B₂O₃=50:50 to 99:1, TiO₂:ZrO₂=50:50 to 99:1, TiO₂:WO₃=50:50 to 99:1.

The carrier according to the present invention can be produced by the following process. At first, alkoxide compounds, chlorides, sulfates, or acetates of elements, which are sources of elements for the carrier, are mixed. The mixture is further mixed with water. Then the mixture is stirred in a state of an aqueous solution or sol to cause hydrolysis. By compositing the oxide using alkoxide or the like as a raw material, which is highly reactive, a state in which the metal is more dispersed in the solution is achieved. Thus, a uniform complex oxide can be obtained, and the content of solid acid in the complex oxide can be increased.

A Ti alkoxide is a compound represented by a general formula Ti(OR¹)₄ (R¹ is an alkyl group having a carbon number of 1 to 20, preferably 2 to 5). Examples of such Ti alkoxide include Ti(OC₂H₅), Ti(O-isoC₃H₇)₄, Ti(O-nC₄H₉)₄, Ti{O—CH₂CH(C₂H₅)C₄H₉}₄, Ti(O—C₃H₃₅)₄, Ti(O-isoC₃H₇)₄, and the like. In addition, Ti sulfates such as TiOSO₄. Ti(SO₄)₂, and the like and Ti acetates such as Ti (OCOCH₃)₄. TiO(OCOCH)₂, Ti₂(OCOCH₃)₆, and the like can be used.

An Si alkoxide is a compound represented by a general formula Si(OR²)₄ (R is an alkyl group having a carbon number of 1 to 20, preferably 1 to 5). Examples of such Si alkoxide include Si(OCH)₄, Si(OC₂H₅)₄, Si(O-isoC₃H₇)₄, Si(O-tertC₄H₉)₄, and the like.

Examples of P alkoxides include P(OCH₃)₃, PO(OCH₃)₃, and the like.

Examples of B alkoxides include B(OCH₃)₃, B(OC₂H₅)₃, and the like.

Examples of Zr alkoxides include Zr(OCH₃)₄, Zr(OC₂H₅)₄, Zr(O-nC₃H₇)₄, Zr(O-isoC₃H₇)₄, Zr(O-nC₄H₉)₄, and the like.

A W alkoxide is a compound represented by a general formula W(OR)₆ (R is an alkyl group having a carbon number of 1 to 20, preferably 1 to 5). Examples of such W alkoxides include W(OCH₃)₄, W(OC₂H₅)₄, W(O-isoC₃H₇)₄, W(O-terC₄H₉)₄, and the like.

The quantity of water associated with the hydrolysis reaction is four times as large as the number of moles of the alkoxide and the like. In order to smoothly run the reaction to obtain a homogeneous carrier, the quantity of water included in the reaction mixture is preferably 10 molar ratio or higher, particularly preferably 40 molar ratio or higher, in relation to the alkoxide and the like. The quantity of water is not limited by a specific upper limit. However, even if the quantity of water is excessively increased, the effect would not especially increase and a large size apparatus may be required. Accordingly, in usual cases, water with the molar ratio of about 300 is sufficient.

It is preferable to run the hydrolysis at 50° C. or higher. More specifically, it is preferable to carry out the hydrolysis at a high temperature because the higher the temperature for hydrolysis is, the finer the crystals produced, and the specific surface area becomes larger. A more preferable range of this temperature is 80 to 100° C.

After the mixed solution is neutralized in a desired manner and precipitates are obtained, the solution is stilled for 5 minutes or more, preferably for 2 hours or more, until the solution is aged. The aging is preferably carried out at a temperature as high as that for the hydrolysis. More specifically, the aging temperature is preferably 50*(7 or higher and ranges more preferably from 80 to 100° C. When the solution is aged, bonds of different carrier elements via an oxygen atom are newly formed and the specific surface area increases.

The sol obtained by the hydrolysis and the subsequent aging is then filtered to obtain a gelatinized material. Then the gelatinized material is washed and calcined. Thus, a TiO₂ carrier, or a carrier consisting of a complex oxide comprising TiO₂ and an M oxide can be obtained. The complex oxide includes an amorphous and/or anatase crystal structure. The burning temperature ranges preferably from 300 to 1,000° C., more preferably from 400 to 550° C., although this temperature may be determined according to the composition ratio or the like of the complex oxide. The burning temperature below 300° C. is not preferable because the calcining cannot be sufficiently carried out. On the other hand, the burning temperature higher than 1,000° C. is also not preferable because the resistance to poisoning by As may degrade due to the decrease of the specific surface area. The burning time ranges preferably from 5 minutes to 24 hours, more preferably from 4 to 5 hours, which may be determined according to the composition ratio of the complex oxide, the burning temperature, and the like. The burning time shorter than the above-described range is not preferable because the calcining cannot be sufficiently carried out. On the other hand, the burning time longer than the above-described range is also not preferable because the resistance to poisoning by As may degrade due to the decrease of the specific surface area.

The carrier according to the present invention may also be produced by a conventionally known coprecipitation method alternatively to the above-described sol-gel method.

By supporting at least one NOx reduction active metal selected from the group consisting of V₂O₅, WO₃, and MoO₃ on the carrier obtained in the above-described manner, a NOx reduction catalyst can be obtained which is capable of efficiently reducing NOx in gases containing NOx, such as NO, NO₂, with ammonium in the presence of oxygen, and having a high resistance to catalyst-poisoning substances such as As contained in flue gases. The NOx reduction catalyst like this can be used as a molded body having a granular shape, a pellet-like shape, a honeycomb shape, or the like. In addition, a NOx reduction catalyst can be obtained by supporting the above-described active metal oxide on a molded carrier prepared by molding an appropriate carrier into the above-described appropriate shape. For the amount of active metal to be supported, the content of active metal included in the catalyst (active metal/(active metal+carrier)×100) is 0.1 to 30% by weight. More specifically, a preferable range is 0.2 to 5% by weight if the active metal is V, 0.1 to 20% by weight if the active metal is Mo, and 5 to 20% by weight if the active metal is W. The method for supporting the active metal is not limited to a specific method and the NOx reduction catalyst can be produced with the active metal supported by a conventional method. The NOx reduction catalyst obtained in the above-described manner can used for flue gases such as boiler flue gases. In particular, the NOx reduction catalyst according to the present invention can be used for flue gases of which the concentration of catalyst-poisoning material such as As included therein is 1 ppm or lower, preferably 100 ppb or lower, in the case of catalyst contact time of about 10,000 hours or more, for example, depending on the catalyst contact time. If the contact time is shorter than this, the NOx reduction catalyst according to the present invention can be used for flue gases of which the concentration of catalyst-poisoning material is as high as about 100 ppm.

Examples [Production of Integrated Honeycomb Molded Carrier and Honeycomb Catalyst] (Preparation of Comparison Carrier 1)

4.4 L of water held at 80° C. was added to 337.6 g of Ti(O-iC₃H₇)₄, which was a Ti source, to cause hydrolysis. Furthermore, the solution was stirred in water held at 80° C. for 2 hours until it was aged. The produced sol was filtered, then the produced alcohol was adequately washed and dried, and then it was calcined by heating at 500° C. for 5 hours.

Ammonium metavanadate (NH₄VO₃) and ammonium paratungstate {(NH₄)₁₀W₁₂O₄₁.5H₂)} were dissolved in a 10 wt % methylamine aqueous solution so that V₂O₅ and WO₃ became 5 and 8 parts by weight, respectively, for 100 parts by weight of TiO₂. Then the mixed solution was impregnated with a TiO₂ powder and dried, and then the resulting material was calcined at 500° C. for 5 hours to obtain a catalyst powder.

3 parts by weight of glass fibers and 3 parts by weight of kaolin as binders, 3 parts by weight of a cellulose acetate as an organic plasticizer, and an ammonia aqueous solution were added to 100 parts by weight of the catalyst powder. Then the mixture was kneaded. The kneaded mass was extruded, then the resulting extruded molded body was dried, and then it was calcined at 500° C. for 5 hours. Thus, a comparison honeycomb molded carrier with lattice spacing (S) of 7.5 mm and the wall thickness (T) of 1.0 mm was obtained (refer to FIG. 1).

(Preparation of Integrated Honeycomb Molded Carriers 1 to 9)

Predetermined amounts of Ti(O-iC₃H₇)₄ as a Ti source, Si(OCH)₃ as an Si source, P(OCH₃)₃ as a P source, B(OCH₃)₃ as a B source, Zr(OCH₃)₄ as a Zr source, and/or ammonium paratungstate {(NH₄)₁₀W₁₂O₄₁.5H₂O} as a source were mixed together so that they were mixed at compounding ratios illustrated in the following Table 3 in terms of the compounding ratio of oxides of the elements. Then the mixture was added to water held at 80° C. to cause hydrolysis. Furthermore, the solution was stirred in water held at 80° C. for 2 hours until it was aged. The produced sol was filtered, then the produced alcohol was sufficiently washed and dried, and then the resulting material was calcined by heating it at 500° C. for 5 hours. Thus, complex oxides 1 to 9 of two- or three-component system were obtained.

Ammonium metavanadate (NH₄VO₃) and ammonium paratungstate {(NH₄)₁₀W₁₂O₄₁.5H₂O} were dissolved in a 10 wt % methylamine aqueous solution so that V₂O₅ and WO₃ became 5 and 8 parts by weight, respectively, for 100 parts by weight of the complex oxides 1 to 9. Then the mixed solution was impregnated with a complex oxide powder and dried, and then the resulting material was calcined at 500° C. for 5 hours to obtain a catalyst powder.

3 parts by weight of glass fibers and 3 parts by weight of kaolin as binders, 3 parts by weight of a, cellulose acetate as an organic plasticizer, and an ammonia aqueous solution were added to 100 parts by weight of the catalyst powder. Then the mixture was kneaded. The kneaded mass was extruded, then the resulting extruded molded body was dried, and then the resulting material was calcined at 500° C. for 5 hours. Thus, integrated honeycomb molded carriers 1 to 9 with lattice spacing (S) of 7.5 mm and the wall thickness (T) of 1.0 mm were obtained (refer to FIG. 1).

(Preparation of Comparison Honeycomb Catalyst and Honeycomb Catalysts 1 to 9)

3.9 g of ammonium metavanadate (NH₄VO₃) and 9.0 g of ammonium paratungstate {(NH₄)₁₀W₁₂O₄₁.5H₂O} were dissolved in 55 mL of a 10 wt % methylamine aqueous solution. The solution was then impregnated with 89.0 g of a powder of the above-described TiO₂ or the respective complex oxides 1 to 9 and dried, and then the resulting material was calcined at 500″C for 5 hours. Thus, a catalyst powder including 3 wt % of V₂O₅ and 8 wt % of WO₃ carried by the carrier was obtained. 80 parts by weight of water was added to 20 parts by weight of the obtained catalyst including V₂O₅ and WO₃. Then, the solution was adequately stirred in a ball mill to obtain a washcoat slurry. The above-described integrated honeycomb-molded carrier was immersed in the washcoat slurry. The integrated honeycomb molded carrier was then taken out from the slurry, the excess slurry was blown off from the carrier, and the integrated honeycomb molded carrier was dried at 200° C. The amount of coating was 50 g per 1 L (by the apparent volume) of the base material, and the obtained coated substances were used as the comparison honeycomb catalyst and the honeycomb catalysts 1 to 9.

(Measurement of Specific Surface Area)

The specific surface area was measured for the comparison honeycomb molded carrier and the integrated honeycomb molded carriers 1 to 9 by a Brunauer-Emmett-Teller (BET) single-point adsorption method (nitrogen gas adsorption method). The measurement conditions were as described below.

TABLE 1 Item Condition Sample amount 0.1 g Pretreatment Purged at 200° C. for 2 hours conditions under nitrogen atmosphere Adsorption −196° C. temperature Desorption Room temperature temperature Detector Thermal conductivity detector (TCD)

(Degree of Deterioration)

The degree of deterioration represents the ratio of degradation of the NOx reduction efficiency occurring after a sample gas containing 200 ppm of As was conducted through the comparison honeycomb catalyst and the honeycomb catalysts 1 to 9 for 1 hour. The degree of deterioration was evaluated by using the following expressions (1) and (2):

Degree of deterioration=(NOx reduction efficiency after conducting As)/(Initial NOx reduction efficiency)  (1)

(NOx reduction efficiency)=[(NOx concentration at reaction tube entry−NOx concentration at reaction tube exit)/(NO concentration at reaction tube entry)]×100  (2).

The conditions for the test for the degree of deterioration and the composition of the sample gas were as follows.

TABLE 2 Item Condition Temperature 150° C. Amount of gas 152 Nm³/h Catalyst shape 150 mm × 150 mm × 750 mm GHSV 4,500 h⁻¹ Superficial 3.3 m/s velocity Gas composition NO: 100 ppm, NH₃: 100 ppm, As: 200 ppm, SO₂: 50 ppm, H₂O: 20%, O₂: 10%, N₂: balance

Table 3 illustrates results of evaluation tests for the degree of deterioration of the comparison honeycomb catalyst and the honeycomb catalysts 1 to 9 obtained based on the comparison honeycomb molded carriers and the integrated honeycomb molded carriers 1 to 9 having various specific surface areas, as results for Comparative Example 1 and Examples 1 to 9.

TABLE 3 Degree of Carrier deterioration Com- specific after applying pounding surface area 200 ppm · H Carrier ratio (m²/g) of As load Comparative TiO₂ system 100 52 0.39 Example 1 Example 1 TiO₂/SiO₂ 80:20 130 0.56 system Example 2 TiO₂/P₂O₅ 60:40 108 0.51 system Example 3 TiO₂/B₂O₃ 50:50 102 0.49 system Example 4 TiO₂/ZrO₂ 50:50 113 0.53 system Example 5 TiO₂/SiO₂/ 85:10:5 155 0.58 ZrO₂ system Example 6 TiO₂/SiO₂/ 90:5:5 147 0.6 ZrO₂ system Example 7 TiO₂/SiO₂/ 57:38:5 146 0.53 P₂O₅ system Example 8 TiO₂/SiO₂/ 47.5:47.5:5 132 0.51 B₂O₃ system Example 9 TiO₂/SiO₂/ 47.5:47.5:5 148 0.54 WO₃ system

According to Table 3, it was observed that the degradation of NOx reduction efficiency occurring after applying As loads was inhibited in correlation with the increase of the specific surface area when a carrier with the specific surface area exceeding 100 m²/g was used.

It was also observed that the degradation of NOx reduction efficiency occurring after applying As loads was inhibited in a three-component system based on TiO₂ (Examples 5 to 9) when the specific surface area was increased, similarly to the case of the two-component system (Examples 1 to 4).

In addition, as illustrated in FIG. 2, it was observed that the specific surface area and the degree of deterioration have a correlation regardless of whether the system was a two-component system or a three-component system or of the type of the element constituting the complex oxide.

REFERENCE SIGNS LIST

S Lattice spacing T Wall thickness 

1-4. (canceled)
 5. A method for reducing NOx from flue gases containing As, the method comprising reducing NOx from the flue gases containing As by using a NOx reduction catalyst in which at least one NOx reduction active metal is supported on a NOx reduction catalyst carrier, wherein the NOx reduction catalyst carrier comprises has a honeycomb structure, and a specific surface area of the NOx reduction catalyst carrier is greater than 100 m²/g.
 6. The method according to claim 5, wherein the NOx reduction catalyst carrier consists of a complex oxide further comprising an oxide of one of two or more elements selected from the group consisting of Si, B, P, Zr and W.
 7. The method according to claim 5, wherein the NOx reduction catalyst carrier consists of a complex oxide further comprising an oxide of two or more elements selected from the group consisting of Si, B, P, Zr, and W.
 8. The method according to claim 5, wherein the NOx reduction catalyst carrier is produced by a coprecipitation method or a sol-gel method.
 9. The method according to claim 5, wherein the flue gases containing As are flue gases from coal-fired boilers.
 10. The method according to claim 6, wherein the NOx reduction catalyst carrier is produced by a coprecipitation method or a sol-gel method.
 11. The method according to claim 7, wherein the NOx reduction catalyst carrier is produced by a coprecipitation method or a sol-gel method.
 12. The method according to claim 6, wherein the flue gases containing As are flue gases from coal-fired boilers.
 13. The method according to claim 7, wherein the flue gases containing As are flue gases from coal-fired boilers.
 14. The method according to claim 8, wherein the flue gases containing As are flue gases from coal-fired boilers. 